USDA-ARS, Water Management Research Unit, San Joaquin Valley Agricultural Sciences Center, Parlier, CA 93648, USA; Department of Plant Sciences, University of California, Davis, Salinas, CA 93905, USA.
Chemosphere. 2013 Oct;93(7):1379-85. doi: 10.1016/j.chemosphere.2013.06.068. Epub 2013 Jul 27.
Raised beds are used to produce some high-value annual fruit and vegetable crops such as strawberry in California (CA) and tomato in Florida (FL), USA. Pre-plant soil fumigation is an important tool to control soil-borne pests in the raised beds. However, fumigant emissions have detrimental environmental consequences. Field trials were conducted to evaluate emissions of 1,3-dichloropropene (1,3-D) and chloropicrin (CP) in two different production systems with raised beds covered by different tarps. In the CA trial, InLine (60.8% 1,3-D and 33.3% CP) was drip-applied at 340 kg ha(-1) to 5 cm deep in the beds (30 cm high and 107 cm wide) tarped with polyethylene (PE) or virtually impermeable film (VIF). In the FL trial, carbonated Telone C35 (63.4% 1,3-D and 34.7% CP) was shank-applied at 151 kg ha(-1) to 20 cm deep in the beds (22 cm high and 76 cm wide) tarped with totally impermeable film (TIF). Emissions from tarped beds relative to furrows were contrary between the two trials. For the CA trial, the emission was 47% of applied 1,3-D and 27% of applied CP from PE tarped beds and 31% of applied 1,3-D and 15% of applied CP from VIF tarped beds, while that from uncovered furrows was<0.4% for both chemicals in both fields. In the FL trial, only 0.1% 1,3-D was emitted from the TIF tarped beds, but 27% was measured from the uncovered furrows. Factors contributing to the differences in emissions were chiefly raised-bed configuration, tarp permeability, fumigant application method, soil properties, soil water content, and fumigant carbonation. The results indicate that strategies for emission reduction must consider the differences in agronomic production systems. Modifying raised bed configuration and fumigant application technique in coarse textured soils with TIF tarping can maximize fumigation efficiency and emission reduction.
在加利福尼亚州(CA)和佛罗里达州(FL),高架床被用于种植一些高价值的一年生水果和蔬菜作物,如草莓和番茄。定植前土壤熏蒸是控制高架床中土壤传播病虫害的重要手段。然而,熏蒸剂的排放会对环境造成不利影响。本研究进行了田间试验,以评估两种不同生产系统中高架床的排放情况,这两种生产系统使用了不同的篷布覆盖高架床。在 CA 试验中,Inline(60.8% 1,3-D 和 33.3% CP)以 340kg/ha 的剂量滴灌施用于深 5cm(高 30cm、宽 107cm)的高架床中,篷布为聚乙烯(PE)或几乎不可渗透的薄膜(VIF)。在 FL 试验中,碳酸 Telone C35(63.4% 1,3-D 和 34.7% CP)以 151kg/ha 的剂量深施于深 20cm(高 22cm、宽 76cm)的高架床中,篷布为完全不可渗透的薄膜(TIF)。两个试验中,篷布覆盖的高架床与垄沟相比,排放情况相反。对于 CA 试验,PE 篷布覆盖的高架床中,施用的 1,3-D 的排放量为 47%,施用的 CP 排放量为 27%;VIF 篷布覆盖的高架床中,施用的 1,3-D 的排放量为 31%,施用的 CP 排放量为 15%,而两个田块中未覆盖的垄沟中,这两种化学物质的排放量均<0.4%。在 FL 试验中,TIF 篷布覆盖的高架床中仅排放了 0.1%的 1,3-D,但从未覆盖的垄沟中测量到 27%的排放量。造成排放差异的因素主要是高架床的配置、篷布的渗透性、熏蒸剂的施用方法、土壤性质、土壤含水量和熏蒸剂的碳酸化。结果表明,减排策略必须考虑农业生产系统的差异。在 TIF 覆盖的粗质地土壤中,通过改变高架床的配置和熏蒸剂的施用技术,可以最大限度地提高熏蒸效率和减少排放。